Destruction of 1,1,1-trichloroethane and 1,2-dichloroethane DNAPLs by catalyzed H2O2 propagations (CHP).

Catalyzed H2O2 propagations (CHP) was studied to treat 1,1,1-trichloroethane (TCA) and 1,1-dichloroethane (DCA) dense nonaqueous phase liquids (DNAPLs) and to elucidate the reactive oxygen species responsible for their destruction. A TCA DNAPL was rapidly destroyed by CHP at a rate 3.5 times greater than its maximum rate of dissolution. Using systems that generate a single reactive oxygen species, the species responsible for TCA DNAPL destruction was found to be superoxide. Both hydroxyl radical and superoxide were responsible for the destruction of the DCA DNAPL. Both compounds were destroyed at equal rates in a mixed TCA/DCA DNAPL, which suggests that the rate of treatment is limited by a surface phenomenon at the DNAPL-water interface. The optimum pH for the destruction of TCA and DCA DNAPLs was near the pKa of 4.8 for perhydroxyl radical-superoxide systems. The results of this research demonsrate that TCA and DCA DNAPLs are effectively destroyed by CHP and that superoxide generation is necessary for effective TCA DNAPL destruction, while both hydroxyl radical and superoxide are necessary for effective DCA DNAPL destruction.

Pyrolusite (beta-MnO2)-mediated, near dry-phase oxidation of 2,4,6-trichlorophenol.

The pyrolusite (beta-MnO2)-mediated oxidation of 2,4,6-trichlorophenol (TCP) under nonaqueous conditions was investigated to assess the potential for abiotic transformations of chlorophenols and their transformation pathways when they are released to soils and the vadose zone. Lower rates of TCP oxidation were found at lower relative humidities, but the rates were still relatively high under near-dry conditions, with 86% of the TCP transformed within 24 h at less than 2% relative humidity. The rates of TCP transformation and soluble manganese formation at less than 2% relative humidity were not affected by atmospheric oxygen content. The manganese oxide-mediated oxidation of TCP resulted in the formation of 2,6-dichloro-1,4-benzoquinone and dimers, including polychlorinated phenoxyphenols and at least one tetrachlorodibenzo-p-dioxin. The products are consistent with the proposed mechanism in which some of the TCP is transformed into trichlorophenoxy radicals that attack TCP and its transformation products. The present results demonstrate that naturally occurring manganese oxides have the potential to oxidize industrial compounds such as TCP; however, the transformation products may be more toxic and persistent than the parent compound.

Mechanism for the destruction of carbon tetrachloride and chloroform DNAPLs by modified Fenton's reagent.

The destruction of a carbon tetrachloride DNAPL and a chloroform DNAPL was investigated in reactions containing 0.5 mL of DNAPL and a solution of modified Fenton's reagent (2M H2O2 and 5mM iron(III)-chelate). Carbon tetrachloride and chloroform masses were followed in the DNAPLs, the aqueous phases, and the off gasses. In addition, the rate of DNAPL destruction was compared to the rate of gas-purge dissolution. Carbon tetrachloride DNAPLs were rapidly destroyed by modified Fenton's reagent at 6.5 times the rate of gas purge dissolution, with 74% of the DNAPL destroyed within 24h. Use of reactions in which a single reactive oxygen species (hydroxyl radical, hydroperoxide anion, or superoxide radical anion) was generated showed that superoxide is the reactive species in modified Fenton's reagent responsible for carbon tetrachloride DNAPL destruction. Chloroform DNAPLs were also destroyed by modified Fenton's reagent, but at a rate slower than the rate of gas purge dissolution. Reactions generating a single reactive oxygen species demonstrated that chloroform destruction was the result of both superoxide and hydroxyl radical activity. Such a mechanism of chloroform DNAPL destruction is in agreement with the slow but relatively equal reactivity of chloroform with both superoxide and hydroxyl radical. The results of this research demonstrate that modified Fenton's reagent can rapidly and effectively destroy DNAPLs of contaminants characterized by minimal reactivity with hydroxyl radical, and should receive more consideration as a DNAPL cleanup technology.

Identification of the reactive oxygen species responsible for carbon tetrachloride degradation in modified Fenton's systems.

The reactive oxygen species responsible for the transformation of carbon tetrachloride (tetrachloromethane, CT) by modified Fenton's reagent using hydrogen peroxide (H2O2) concentrations >0.1 M was investigated. Addition of the hydroxyl radical scavenger 2-propanol to modified Fenton's reactions did not significantly lower CT transformation rates. Scavenging by 2-propanol not only confirmed that hydroxyl radicals are not responsible for CT destruction, but also suggested that a major product of an iron (III)-driven initiation reaction, superoxide radical anion (O2-), is the species responsible for CT transformation. To investigate this hypothesis, CT degradation was studied in aqueous KO2 reactions. Minimal CT degradation was found in CT-KO2 reactions; however, when H2O2 was added to the KO2 reactions at concentrations similar to those in the modified Fenton's reactions (0.1, 0.5, and 1 M), CT degradation increased significantly. Similar results were obtained when 1 M concentrations of other solvents were added to aqueous KO2 reactions, and the observed first-order rate constant for CT degradation correlated strongly (R2 = 0.986) with the empirical solvent polarity (E(T)N) of the added solvents. The results indicate that even dilute concentrations of solvents, including H202, can increase the reactivity of O2- in water, probably by changing its solvation sphere. The higher reactivity of O2- generated in modified Fenton's reagent, which has a less polar nature due to the presence of H2O2, may result in a wider range of contaminant degradation than previously thought possible.